GreenWater Laboratories/CyanoLab, 205 Zeagler Drive, Palatka, FL, 32177, United States.
Norwegian Veterinary Institute, P. O. Box 750 Sentrum, N-0106, Oslo, Norway; Measurement Science and Standards, National Research Council, 1411 Oxford Street, Halifax, NS, B3H 3Z1, Canada.
Harmful Algae. 2018 Dec;80:117-129. doi: 10.1016/j.hal.2018.10.006. Epub 2018 Nov 3.
In the summer of 2012, over 750 dead and dying birds were observed at the Paul S. Sarbanes Ecosystem Restoration Project at Poplar Island, Maryland, USA (Chesapeake Bay). Clinical signs suggested avian botulism, but an ongoing dense Microcystis bloom was present in an impoundment on the island. Enzyme-linked immunosorbent assay (ELISA) analysis of a water sample indicated 6000 ng mL of microcystins (MCs). LC-UV/MS analysis confirmed the presence of MC-LR and a high concentration of an unknown MC congener (m/z 1037.5). The unknown MC was purified and confirmed to be [D-Leu]MC-LR using NMR spectroscopy, LC-HRMS and LC-MS, which slowly converted to [D-Leu,Glu(OMe)]MC-LR during storage in MeOH. Lyophilized algal material from the bloom was further characterized using LC-HRMS and LC-MS in combination with chemical derivatizations, and an additional 24 variants were detected, including MCs conjugated to Cys, GSH and γ-GluCys and their corresponding sulfoxides. Mallard (Anas platyrhynchos) livers were tested to confirm MC exposure. Two broad-specificity MC ELISAs and LC-MS were used to measure free MCs, while 'total' MCs were estimated by both MMPB (3-methoxy-2-methyl-4-phenylbutyric acid) and thiol de-conjugation techniques. Free microcystins in the livers (63-112 ng g) accounted for 33-41% of total microcystins detected by de-conjugation and MMPB techniques. Free [D-Leu]MC-LR was quantitated in tissues at 25-67 ng g (LC-MS). The levels of microcystin varied based on analytical method used, highlighting the need to develop a comprehensive analysis strategy to elucidate the etiology of bird mortality events when microcystin-producing HABs are present.
2012 年夏天,在美国马里兰州切萨皮克湾的波托马克岛的保罗·S·萨班斯生态系统恢复项目中,观察到 750 多只死亡和垂死的鸟类(Chesapeake Bay)。临床症状表明存在鸟源性肉毒中毒,但岛上的一个蓄水坝中存在持续的密集微囊藻水华。对水样的酶联免疫吸附测定(ELISA)分析表明微囊藻毒素(MCs)的含量为 6000ng/mL。LC-UV/MS 分析证实存在 MC-LR 和一种高浓度的未知 MC 同系物(m/z 1037.5)。该未知 MC 通过 NMR 光谱、LC-HRMS 和 LC-MS 进行了纯化和确证,为[D-Leu]MC-LR,在甲醇中储存期间,其缓慢转化为[D-Leu,Glu(OMe)]MC-LR。使用 LC-HRMS 和 LC-MS 结合化学衍生化,进一步对来自水华的冻干藻类材料进行了表征,并检测到另外 24 种变体,包括与 Cys、GSH 和γ-GluCys 共轭的 MC 及其相应的亚砜。对野鸭(Anas platyrhynchos)肝脏进行了测试,以确认 MC 暴露。使用两种宽特异性 MC ELISA 和 LC-MS 来测量游离 MC,而 MMPB(3-甲氧基-2-甲基-4-苯基丁酸)和巯基去共轭技术则用于估计“总”MC。肝脏中游离微囊藻毒素(63-112ng/g)占去共轭和 MMPB 技术检测到的总微囊藻毒素的 33-41%。游离[D-Leu]MC-LR 在组织中用 LC-MS 定量为 25-67ng/g。微囊藻毒素的水平取决于所使用的分析方法,这突出表明,当存在产生微囊藻毒素的赤潮时,需要开发一种全面的分析策略来阐明鸟类死亡事件的病因。